Application of a constrained regularization method to extraction of affinity distributions: Proton and metal binding to humic substances
The binding of proton and metal cations to humic substances has been analyzed with a regularized fitting procedure (using the CONTIN software package) to extract conditional affinity distributions, valid at a given ionic strength, from binding (titration) curves. The procedure was previously tested...
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2009
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| LEADER | 14692caa a22019697a 4500 | ||
|---|---|---|---|
| 001 | PAPER-8568 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518203822.0 | ||
| 008 | 190411s2009 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-67649295310 | |
| 024 | 7 | |2 cas |a fulvic acid, 479-66-3; lead, 7439-92-1; phenol, 108-95-2, 3229-70-7; proton, 12408-02-5, 12586-59-3 | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 030 | |a JCISA | ||
| 100 | 1 | |a Orsetti, S. | |
| 245 | 1 | 0 | |a Application of a constrained regularization method to extraction of affinity distributions: Proton and metal binding to humic substances |
| 260 | |c 2009 | ||
| 270 | 1 | 0 | |m Molina, F.V.; INQUIMAE, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Pabellon II, Buenos Aires C1428EHA, Argentina; email: fmolina@qi.fcen.uba.ar |
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| 520 | 3 | |a The binding of proton and metal cations to humic substances has been analyzed with a regularized fitting procedure (using the CONTIN software package) to extract conditional affinity distributions, valid at a given ionic strength, from binding (titration) curves. The procedure was previously tested with simulated titration curves using a simple bi-Gaussian model, the NICA-Donnan model, and the Stockholm humic model. Application to literature data for proton binding shows that in several cases the affinity distribution found is bimodal (carboxylic and phenolic sites) as usually assumed; however in other cases, specially for fulvic acids, a trimodal distribution is clearly discerned, with a smaller peak between the two noted above attributed to the presence of vicinal carboxylic groups. The analysis of metal binding curves has been performed in a few cases where the available data could be reliably processed, separating the proton affinity distribution and obtaining the conditional affinity spectra. For Cd(II) and Pb(II) a bimodal distribution is found, attributed in principle to mono- and bidentate binding, based on spectroscopic data. In the case of Cu(II), a more complex affinity distribution is found showing 3-4 peaks; this is consistent with spectroscopic studies, where different binding modes, up to tetradentate, have been observed. © 2009 Elsevier Inc. All rights reserved. |l eng | |
| 536 | |a Detalles de la financiación: Agencia Nacional de Promoción Científica y Tecnológica, 06-12467 | ||
| 536 | |a Detalles de la financiación: Universidad de Buenos Aires, UBACYT 2004-2007 X105, 2008-2010 X148 | ||
| 536 | |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, PIP 05216 | ||
| 536 | |a Detalles de la financiación: The authors gratefully acknowledge financial support from the Universidad de Buenos Aires (UBACYT 2004-2007 X105 and 2008-2010 X148), the Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET, PIP 05216). and the Agencia Nacional de Promoción Científica y Tecnológica (Grant No. 06-12467). F.V.M. is a member of the Carrera del Investigador Científico of CONICET. Appendix A | ||
| 593 | |a INQUIMAE, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Pabellon II, Buenos Aires C1428EHA, Argentina | ||
| 690 | 1 | 0 | |a BINDING EQUILIBRIUM |
| 690 | 1 | 0 | |a CONTIN |
| 690 | 1 | 0 | |a HUMIC SUBSTANCES |
| 690 | 1 | 0 | |a POLLUTANT RETENTION |
| 690 | 1 | 0 | |a SOIL ORGANIC MATTER |
| 690 | 1 | 0 | |a BINDING EQUILIBRIUM |
| 690 | 1 | 0 | |a CONTIN |
| 690 | 1 | 0 | |a HUMIC SUBSTANCES |
| 690 | 1 | 0 | |a POLLUTANT RETENTION |
| 690 | 1 | 0 | |a SOIL ORGANIC MATTER |
| 690 | 1 | 0 | |a BINDING ENERGY |
| 690 | 1 | 0 | |a BIOGEOCHEMISTRY |
| 690 | 1 | 0 | |a BIOLOGICAL MATERIALS |
| 690 | 1 | 0 | |a CURVE FITTING |
| 690 | 1 | 0 | |a IONIC STRENGTH |
| 690 | 1 | 0 | |a METAL RECOVERY |
| 690 | 1 | 0 | |a ORGANIC ACIDS |
| 690 | 1 | 0 | |a ORGANIC POLLUTANTS |
| 690 | 1 | 0 | |a PHENOLS |
| 690 | 1 | 0 | |a PROTONS |
| 690 | 1 | 0 | |a SOILS |
| 690 | 1 | 0 | |a SPECTROSCOPIC ANALYSIS |
| 690 | 1 | 0 | |a TITRATION |
| 690 | 1 | 0 | |a WASTE INCINERATION |
| 690 | 1 | 0 | |a BINDING SITES |
| 690 | 1 | 0 | |a CARBOXYLIC ACID |
| 690 | 1 | 0 | |a FULVIC ACID |
| 690 | 1 | 0 | |a LEAD |
| 690 | 1 | 0 | |a PHENOL |
| 690 | 1 | 0 | |a PROTON |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a BINDING AFFINITY |
| 690 | 1 | 0 | |a COMPUTER PROGRAM |
| 690 | 1 | 0 | |a COMPUTER SIMULATION |
| 690 | 1 | 0 | |a CONSTRAINED REGULARIZATION METHOD |
| 690 | 1 | 0 | |a HUMIC SUBSTANCE |
| 690 | 1 | 0 | |a IONIC STRENGTH |
| 690 | 1 | 0 | |a METAL BINDING |
| 690 | 1 | 0 | |a METHODOLOGY |
| 690 | 1 | 0 | |a NORMAL DISTRIBUTION |
| 690 | 1 | 0 | |a PRIORITY JOURNAL |
| 690 | 1 | 0 | |a RELIABILITY |
| 690 | 1 | 0 | |a SPECTROSCOPY |
| 690 | 1 | 0 | |a STATISTICAL MODEL |
| 690 | 1 | 0 | |a VALIDATION PROCESS |
| 700 | 1 | |a Andrade, E.M. | |
| 700 | 1 | |a Molina, F.V. | |
| 773 | 0 | |d 2009 |g v. 336 |h pp. 377-387 |k n. 2 |p J. Colloid Interface Sci. |x 00219797 |w (AR-BaUEN)CENRE-15 |t Journal of Colloid and Interface Science | |
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| 856 | 4 | 0 | |u https://doi.org/10.1016/j.jcis.2009.04.049 |y DOI |
| 856 | 4 | 0 | |u https://hdl.handle.net/20.500.12110/paper_00219797_v336_n2_p377_Orsetti |y Handle |
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